LTERN Data Portal
Woodland Restoration Plot Network: Bird Survey Data (Spring), Western Sydney Parklands (Western Sydney Regional Park), Australia, 2013
- Citation
-
Keith, D; Wilkins, K (): Woodland Restoration Plot Network: Bird Survey Data (Spring), Western Sydney Parklands (Western Sydney Regional Park), Australia, 2013. Long Term Ecological Research Network. http://www.ltern.org.au/knb/metacat/ltern2.203.77/html
- Identifier
-
- docid
- ltern2.203.77
- Data Creators
-
- Individual
- Professor David Keith
- Position
- Plot Leader
- Organization
- Centre for Ecosystem Science, University of New South Wales
- Individual
- Katy Wilkins
- Position
- Research Assistant
- Organization
- Centre for Ecosystem Science
- Abstract
-
The Woodland Restoration Plot Network Spring Bird Survey Data Package contains bird point count survey data for thirty-six 0.1 hectare sites which were established on retired farmland that includes a mosaic of restored vegetation (native plantings) of varying ages juxtaposed with patches of remnant vegetation and untreated, abandoned pasture. All sites were originally woodland prior to agricultural development about 200 years ago. The Woodland Restoration Plot Network research plots commenced in 1992 and have been revisited every 3-4 years since 2001. A synopsis of related data packages which have been collected as part of the Woodland Restoration Plot Network’s full program is provided at http://www.ltern.org.au/index.php/ltern-plot-networks/woodland-restoration
- Contacts for Questions on the Use and Interpretation of Data
-
- Individual
- Katy Wilkins
- Position
- Research Assistant
- Organization
- Centre for Ecosystem Science
- Address
-
Centre for Ecosystem Science
School of Biological, Earth and Environmental Sciences, University of New South Wales
Sydney. NSW 2052
- Phone
-
- voice
- 02 9385 8296
- Email Address
- k.wilkins@unsw.edu.au
- Individual
- Professor David Keith
- Position
- Plot Leader
- Organization
- Centre for Ecosystem Science, University of New South Wales
- Address
-
Centre for Ecosystem Science, School of Biological, Earth and Environmental Sciences
University of New South Wales
Sydney. NSW 2052
Australia
- Phone
-
- voice
- 02 9385 2111
- Email Address
- david.keith@unsw.edu.au
- Individual
- Chris Simpson
- Position
- Research Assistant
- Organization
- Centre for Ecosystem Science
- Address
-
Centre for Ecosystem Science
School of Biological, Earth and Environmental Sciences, University of New South Wales
Sydney. NSW 2052
- Phone
-
- voice
- 0409 159 334
- Email Address
- Christopher.Simpson@unsw.edu.au
- Individual
- Renee Woodward
- Position
- Research Assistant
- Organization
- Centre for Ecosystem Science
- Address
-
Centre for Ecosystem Science
School of Biological, Earth and Environmental Sciences, University of New South Wales
Sydney. NSW 2052
- Phone
-
- voice
- 02 9585 6051
- Email Address
- r.woodward@unsw.edu.au
- Project Information and Data Owners
-
- Title
- Woodland Restoration Plot Network
- Personnel
-
- Role
- Data Owner
- Individual
- Professor David Keith
- Position
- Plot Leader
- Organization
- Centre for Ecosystem Science, University of New South Wales
- Role
- Research Assistant
- Individual
- Chris Simpson
- Position
- Research Assistant
- Organization
- Centre for Ecosystem Science
- Role
- Research Assistant
- Individual
- Renee Woodward
- Position
- Research Assistant
- Organization
- Centre for Ecosystem Science
- Role
- Research Assistant
- Individual
- Katy Wilkins
- Position
- Research Assistant
- Organization
- Centre for Ecosystem Science
- Funding
-
Since 2012 this project has been part of the Long Term Ecological Research Network (LTERN). This work was supported by the Australian Government’s Terrestrial Ecosystems Research Network (www.tern.org.au) – an Australian research infrastructure facility established under the National Collaborative Research Infrastructure Strategy and Education Infrastructure Fund–Super Science Initiative through the Department of Industry, Innovation, Science, Research and Tertiary Education.
- Methods and Sampling Information
-
- Methods
-
Method Step 1
- Description
-
Plot set-up
Thirty-six 0.1 hectare sites which were established on retired farmland that includes a mosaic of restored vegetation (native plantings) of varying ages juxtaposed with patches of remnant vegetation and untreated, abandoned pasture. All sites were originally woodland prior to agricultural development about 200 years ago. This is part of a larger dataset that spans from 1992.
- Instrument
-
- Global Positioning Systems, Compass, Tape Measure, marking tape
Method Step 2- Description
-
Bird point count survey
Bird point count survey methods were employed (Pyke and Recher 1984). Point Count Stations are located within the centre of the 20 x 20 m floristic plots. After a one minute settling time, an observer surveys the area surrounding the Point Count Station for a 20 minute period. The species (and the sex and age if appropriate), method (visual or auditory), time (0-3 mins; 3-5 mins; 5-10 mins; 10-15 mins; 15- 20 mins), stratum (canopy; upper-understorey, mid-understorey, lower-understorey; ground), distance (<10 m; 10–20 m; 20–30 m; > 30 m) and orientation (N; NE; E; SE; S; SW; W; NW) from observer, and activity type, is recorded for the birds detected. Fly-overs, juveniles and flushes are recorded separately. Each of the Point Count Stations are surveyed a minimum of six times by two independent observers between sunrise and 10:00 am within a seasonal period. Sites within 500 m of each other are not surveyed during the same morning, and wherever possible, each station is surveyed at a different time on subsequent visits. The starting time, weather conditions (approx. temp, wind strength, precipitation), presence of flowering or fruiting plants, and an estimate of ambient noise is also recorded. Surveys are not conducted on days of rain (more than a drizzle), high wind, or fog.
The Woodland Restoration Plot Network research plots commenced in 1992 and have been revisited every 3-4 years since 2001.
See Pyke GH, Recher HF (1984) Methods of censusing birds in Australia : proceedings of a symposium organised jointly by the Zoology Section of the ANZAAS and the Western Australian Group of the Royal Australasian Ornithologists Union, May 17 1983. In. ' Ed. SJJF Davies) pp. 55-63. (Dept of Conservation and Environment with the Royal Australasian Ornithologists
Union)
- Sampling
-
- Study Extent Description
-
The study site is located on retired farmland that includes a mosaic of restored vegetation (native plantings) of varying ages juxtaposed with patches of remnant vegetation and untreated, abandoned pasture. During their period of pastoral management (prior to 1990), the sites have been grazed by cattle, fertilised and planted with exotic pasture grasses, particularly Phalaris species. All sites were originally woodland prior to agricultural development about 200 years ago. Restoration projects commenced in the area in 1992 with a stated goal of ‘re-establishment of native vegetation’ (Perkins 1997). The restoration plantings were carried out in a pattern designed to connect remnant patches of woodland, which were also the primary sources of seed for tubestock. To evaluate success against the defined goal, we therefore identified the remnants as suitable reference sites to which the restored sites were expected to increase their resemblance in composition and structure over time. Disturbance resulting from past agricultural practices in the area have impacted upon remnant patches to varying degrees, but these were the best available examples of native woodland in the region. Untreated pasture is defined as a control, from which restored sites are expected to become increasingly dissimilar in species composition and vegetation structure with time.
- Sampling Description
-
The restoration process was initiated with exclusion of livestock and weed control (J. Christie, Greening Australia, pers. comm.). All sites were slashed and sprayed with glyphosate before planting was undertaken. Twenty-six indigenous trees and shrub species, propagated to tubestock from local seed sources, were planted mechanically in rows after the pasture began to break down. The mix of planted species varied across the landscape, the aim being to match species with soils and topographic positions occupied by their wild populations. All plants were weed matted with a recycled paper disc and surrounded by a protective plastic sleeve. Maintenance sprays of glyphosate were applied in spring and autumn for two-three years after planting to reduce competition from weeds in the vicinity of plants. To reduce the risk of fire, mechanical slashing was carried out amongst the plantings and hazard reduction fires were lit in areas surrounding plantings at approximately annual intervals. Since the late 1990s, cattle have been reintroduced into the southern areas of plantings, but fencing has been constructed to exclude livestock from some restoration areas and remnants (D. Williams, Greening Australia, pers. comm.). Cattle continue to be excluded from the northern areas of plantings. The study landscape therefore comprises a mosaic of patches including untreated pastures, remnant woodlands with various histories of past disturbance and a chronosequence of restoration plantings with dates of origin from 1992 to 2002. The aims of the study design were to sample management treatments (untreated pasture, the chronosequence of restored vegetation and remnant woodland) across four primary locations (Hoxton Park, Plough and Harrow Property, Western Sydney Regional Park and Prospect Reservoir). A fully randomised orthogonal sampling design was not possible because all management treatments were not represented at each of the four primary locations. Sample sites representing different management treatments were therefore situated haphazardly within patches, to sample areas with similar topography (upper and mid slopes) to minimise environmental variation that may potentially confound management effects. The first set of vegetation surveys were carried out in 2001 (25 sites), with repeat surveys of new haphazardly selected sites to sample the same patch types in 2004 (54 sites), 2009 (24 sites) and 2012 (36 sites). The total number of sites varied between surveys depending on available resources, but the proportional stratification among patch types and ages remained the same. Invertebrates were sampled in late 2002 and 2009. Soils were sampled in 2010 by collaborators at UWS. A survey of avifauna commenced in 2013.
- Keywords and Subject Categories
-
- LTERN Monitoring Themes
-
- Birds
- Invasive animals
- ANZSRC-FOR
-
- 0501
- 0602
- 0608
- GCMD
-
- Earth Science > Biological Classification > Animals/Vertebrates > Birds
- Geographic Coverage
-
- Geographic Description
- Western Sydney Parklands (Western Sydney Regional Park), Australia
- Bounding Coordinates
-
- West
- 150.817755 degrees
- East
- 150.871493 degrees
- North
- -33.844866 degrees
- South
- -33.908897 degrees
- Temporal Coverage
-
- Date Begin
- 2013-10-28
- Date End
- 2013-12-11
- Taxonomic Coverage and Classification
-
- Classification
-
-
- Species
- Acanthiza chrysorrhoa
-
- Species
- Acanthiza lineata
-
- Species
- Acanthiza nana
-
- Species
- Acanthiza reguloides
-
- Species
- Acanthorhynchus tenuirostris
-
- Species
- Accipiter fasciatus
-
- Species
- Acrocephalus stentoreus
-
- Species
- Alisterus scapularis
-
- Species
- Anas superciliosa
-
- Species
- Anthochaera carunculata
-
- Species
- Ardea ibis
-
- Species
- Ardea intermedia
-
- Species
- Ardea modesta
-
- Species
- Ardea pacifica
-
- Species
- Cacatua galerita
-
- Species
- Cacatua sanguinea
-
- Species
- Cacatua tenuirostris
-
- Species
- Cacomantis flabelliformis
-
- Species
- Cacomantis variolosus
-
- Species
- Carduelis carduelis
-
- Species
- Chalcites basalis
-
- Species
- Chalcites lucidus
-
- Species
- Chenonetta jubata
-
- Species
- Cisticola exilis
-
- Species
- Colluricincla harmonica
-
- Species
- Coracina novaehollandiae
-
- Species
- Coracina papuensis
-
- Species
- Corvus coronoides
-
- Species
- Coturnix ypsilophora
-
- Species
- Cracticus tibicen
-
- Species
- Cracticus torquatus
-
- Species
- Dacelo novaeguineae
-
- Species
- Dicaeum hirundinaceum
-
- Species
- Egretta novaehollandiae
-
- Species
- Elanus axillaris
-
- Species
- Eolophus roseicapillus
-
- Species
- Eopsaltria australis
-
- Species
- Eudynamys orientalis
-
- Species
- Eurystomus orientalis
-
- Species
- Falco berigora
-
- Species
- Falco longipennis
-
- Species
- Falcunculus frontatus
-
- Species
- Geopelia humeralis
-
- Species
- Gerygone albogularis
-
- Species
- Gerygone mouki
-
- Species
- Glossopsitta concinna
-
- Species
- Glossopsitta pusilla
-
- Species
- Grallina cyanoleuca
-
- Species
- Hirundapus caudacutus
-
- Species
- Hirundo neoxena
-
- Species
- Lalage sueurii
-
- Species
- Lichenostomus chrysops
-
- Species
- Lichenostomus penicillatus
-
- Species
- Malurus cyaneus
-
- Species
- Malurus lamberti
-
- Species
- Manorina melanocephala
-
- Species
- Manorina melanophrys
-
- Species
- Melithreptus lunatus
-
- Species
- Monarcha melanopsis
-
- Species
- Myiagra rubecula
-
- Species
- Myzomela sanguinolenta
-
- Species
- Neochmia temporalis
-
- Species
- Ocyphaps lophotes
-
- Species
- Oriolus sagittatus
-
- Species
- Pachycephala pectoralis
-
- Species
- Pachycephala rufiventris
-
- Species
- Pardalotus punctatus
-
- Species
- Pardalotus striatus
-
- Species
- Pelecanus conspicillatus
-
- Species
- Petrochelidon nigricans
-
- Species
- Phalacrocorax varius
-
- Species
- Platycercus eximius
-
- Species
- Podargus strigoides
-
- Species
- Porphyrio porphyrio
-
- Species
- Psephotus haematonotus
-
- Species
- Psophodes olivaceus
-
- Species
- Pycnonotus jocosus
-
- Species
- Rhipidura albiscapa
-
- Species
- Rhipidura leucophrys
-
- Species
- Rhipidura rufifrons
-
- Species
- Scythrops novaehollandiae
-
- Species
- Sericornis frontalis
-
- Species
- Smicrornis brevirostris
-
- Species
- Strepera graculina
-
- Species
- Streptopelia chinensis
-
- Species
- Sturnus tristis
-
- Species
- Sturnus vulgaris
-
- Species
- Tachybaptus novaehollandiae
-
- Species
- Taeniopygia bichenovii
-
- Species
- Threskiornis molucca
-
- Species
- Trichoglossus haematodus
-
- Species
- Turdus merula
-
- Species
- Zosterops lateralis
-
- Intellectual Rights, Licence and Usage Conditions
-
CC-BY-4_0 Special conditions Prior to publication of research utilising this data, the data provider (David Keith) requests consultation. Spatial coordinates for site codes (site_number) are available at http://www.ltern.org.au/knb/metacat/ltern.127/html, in the table titled "kwrt_spatial_data_2011-2014_p174t1180.csv".
- Data Table
-
- Name
- kwrt_birds_spring_2013_p12t312.csv
- Attribute Information
-
species_code
- Name
- species_code
- Definition
- Species code
- Measurement Type
- nominal
- Measurement Domain
-
- Text Domain
-
- Definition
- Character
letter_code- Name
- letter_code
- Definition
- Species alphabetical code
- Measurement Type
- nominal
- Measurement Domain
-
- Text Domain
-
- Definition
- Character
common_name- Name
- common_name
- Definition
- Species common name
- Measurement Type
- nominal
- Measurement Domain
-
- Text Domain
-
- Definition
- Character
scientific_name- Name
- scientific_name
- Definition
- Species scientific name
- Measurement Type
- nominal
- Measurement Domain
-
- Text Domain
-
- Definition
- Character
site_name- Name
- site_name
- Definition
- Site name
- Measurement Type
- nominal
- Measurement Domain
-
- Text Domain
-
- Definition
- Character
count_best- Name
- count_best
- Definition
- Best estimate count
- Measurement Type
- ratio
- Measurement Domain
-
- Standard Unit
- number
- Number Type
- natural
count_lower- Name
- count_lower
- Definition
- Estimated species counts – lower bound
- Measurement Type
- ratio
- Measurement Domain
-
- Standard Unit
- number
- Number Type
- natural
count_upper- Name
- count_upper
- Definition
- Estimated species counts – upper bounds
- Measurement Type
- ratio
- Measurement Domain
-
- Standard Unit
- number
- Number Type
- natural
patch_type- Name
- patch_type
- Definition
- Patch Type
- Measurement Type
- nominal
- Measurement Domain
-
- Enumerated Domain
-
- Code Definition
-
- 1
- Remnant
- 2
- Planting
- 3
- Pasture
stand_age- Name
- stand_age
- Definition
- Stand age in years. 0–99 years — pasture assigned age. 100 years — remnant assigned age.
- Measurement Type
- ratio
- Measurement Domain
-
- Standard Unit
- nominalYear
- Number Type
- whole
grazing- Name
- grazing
- Definition
- Presence or absence of evidence of grazing
- Measurement Type
- nominal
- Measurement Domain
-
- Enumerated Domain
-
- Code Definition
-
- 0
- Not Grazed
- 1
- Grazed
visit- Name
- visit
- Definition
- Sequential visit number - Point Count Stations surveyed a minimum of six times by two independent observers between sunrise and 10:00 am within a seasonal period.
- Measurement Type
- nominal
- Measurement Domain
-
- Text Domain
-
- Definition
- Character
season- Name
- season
- Definition
- Season
- Measurement Type
- nominal
- Measurement Domain
-
- Enumerated Domain
-
- Code Definition
-
- spring
- Spring
- winter
- Winter
survey_date- Name
- survey_date
- Definition
- Survey date
- Measurement Type
- dateTime
- Measurement Domain
-
- Format
- YYYY-MM-DD
observer_initials- Name
- observer_initials
- Definition
- Observer Initials
- Measurement Type
- nominal
- Measurement Domain
-
- Text Domain
-
- Definition
- Character
observation_type- Name
- observation_type
- Definition
- Observation type
- Measurement Type
- nominal
- Measurement Domain
-
- Enumerated Domain
-
- Code Definition
-
- 1
- Seen
- 2
- Heard
- 3
- Heard then seen
identification_confidence- Name
- identification_confidence
- Definition
- Identification confidence
- Measurement Type
- nominal
- Measurement Domain
-
- Enumerated Domain
-
- Code Definition
-
- 0
- Less than 30% confident or unknown
- 1
- 90-100% Confident
- 2
- 60-90% Confident
- 3
- 30-60% Confident
time_of_first_observation- Name
- time_of_first_observation
- Definition
- Time of first observation
- Measurement Type
- nominal
- Measurement Domain
-
- Enumerated Domain
-
- Code Definition
-
- 1
- 0-3=
- 2
- 4-5
- 3
- 6-10
- 4
- 11-15
- 5
- 16-20
distance- Name
- distance
- Definition
- Distance of observation
- Measurement Type
- nominal
- Measurement Domain
-
- Enumerated Domain
-
- Code Definition
-
- 1
- Within 10 metres of the point count station
- 2
- Between 10-20 metres from the point count station
- 3
- Between 20-30 metres from the point count station
- 4
- Greater than 30 metres from the point count station
- 5
- Greater than 500 metres from the point count station
flyover- Name
- flyover
- Definition
- Flyover
- Measurement Type
- nominal
- Measurement Domain
-
- Enumerated Domain
-
- Code Definition
-
- 0
- NA
- 1
- within 30 metres of the point count station
- 2
- greater than 30 metres from the point count station
- 3
- greater than 500 metres from the point count station
temperature- Name
- temperature
- Definition
- Temperature
- Measurement Type
- nominal
- Measurement Domain
-
- Enumerated Domain
-
- Code Definition
-
- 1
- Very cold
- 2
- Very cold - cold
- 3
- Cold
- 4
- Cold - mild
- 5
- Mild
- 6
- Mild - warm
- 7
- Warm
- 8
- Warm to hot
- 9
- Hot
cloud_cover- Name
- cloud_cover
- Definition
- Cloud cover
- Measurement Type
- nominal
- Measurement Domain
-
- Enumerated Domain
-
- Code Definition
-
- 0
- Clear
- 1
- ¼
- 2
- ½
- 3
- ¾
- 4
- Total Cover
wind- Name
- wind
- Definition
- Wind
- Measurement Type
- nominal
- Measurement Domain
-
- Enumerated Domain
-
- Code Definition
-
- a
- 0 (nil)
- b
- 0-1 (nil to leaves rustle)
- c
- 0-2 (nil to branches move)
- d
- 0-3 (nil to large branches move)
- e
- 0-4 (nil to very occasional large gust)
- f
- 1 (leaves rustle)
- g
- 1-2 (leaves rustle to branches move)
- h
- 1-3 (leaves rustle to large branches move)
- i
- 1-4 (leaves rustle to very occasional large gust)
- j
- 2 (branches move)
- k
- 2-3 (branches move to large branches move)
- l
- 2-4 (branches move to very occasional large gust)
- m
- 3 (large branches move)
rain- Name
- rain
- Definition
- Rain
- Measurement Type
- nominal
- Measurement Domain
-
- Enumerated Domain
-
- Code Definition
-
- a
- 0 (nil)
- b
- 0-1 (nil to drizzle)
- c
- 0-2 (nil to rainy)
- d
- 1 (drizzle)
- e
- 1-2 (drizzle to rainy)
- f
- 2 (rainy)
ambient_noise- Name
- ambient_noise
- Definition
- Ambient noise
- Measurement Type
- nominal
- Measurement Domain
-
- Enumerated Domain
-
- Code Definition
-
- 1
- Low - very low
- 2
- Very low
- 3
- Very low - low
- 4
- Low
- 5
- Low - moderate
- 6
- Moderate
- 7
- High
- 8
- High - very high
- 9
- Very high
fruit_flowers- Name
- fruit_flowers
- Definition
- Fruit/ flowers
- Measurement Type
- nominal
- Measurement Domain
-
- Enumerated Domain
-
- Code Definition
-
- 0
- Nil
- 1
- Flowers
- 2
- Fruit
- 3
- Flowers and fruit
- Physical Structure Description
-
- Object Name
- kwrt_birds_spring_2013_p12t312.csv
- Text Format
-
- Number of Header Lines
- 1
- Number of Footer Lines
- 0
- Record Delimiter
- \r\n
- Attribute Orientation
- column
- Simple Delimited
-
- Field Delimiter
- ,
- Distribution
-
Online
- URL
- ltern2.204.7
- Access
-
- Access Control
-
- Auth System
- knb
- Order
- allowFirst
- Allow:
-
Permission Principal [all] cn=submitters,o=unaffiliated,dc=ecoinformatics,dc=org [read] cn=pn_woodland_restoration,o=unaffiliated,dc=ecoinformatics,dc=org [read] cn=allusers,o=unaffiliated,dc=ecoinformatics,dc=org
- Additional Metadata Links
-
additionalLinksAdditional Metadata : additionalLinks
- Metadata
-
- additionalLinks
-
- url
-
- @name
- Woodland Restoration Plot Network homepage
- Access
-
- Access Control
-
- Auth System
- knb
- Order
- allowFirst
- Allow:
-
Permission Principal [read] public [all] cn=submitters,o=unaffiliated,dc=ecoinformatics,dc=org [read] cn=pn_woodland_restoration,o=unaffiliated,dc=ecoinformatics,dc=org
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